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Air quality expert group - Fine particulate matter (PM2.5) in ... - Defra

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<strong>PM2.5</strong> <strong>in</strong> the UK<br />

92<br />

37. Further consideration of all these aspects of emission <strong>in</strong>ventory uncerta<strong>in</strong>ties can<br />

be found <strong>in</strong> Annex D of the report Evaluat<strong>in</strong>g the Performance of <strong>Air</strong> Quality<br />

Models (<strong>Defra</strong>, 2010) which gives some detail of the uncerta<strong>in</strong>ties <strong>in</strong> the spatial<br />

and temporal variability <strong>in</strong> emissions <strong>in</strong> the context of modell<strong>in</strong>g uncerta<strong>in</strong>ties.<br />

38. The NAEI only estimates emissions from sources which need to be <strong>in</strong>cluded<br />

<strong>in</strong> national <strong>in</strong>ventory report<strong>in</strong>g under various <strong>in</strong>ternational commitments<br />

(e.g. CLRTAP) and/or where at least some <strong>in</strong>formation is available to make<br />

a reasonable estimate. Gaps <strong>in</strong> the <strong>in</strong>ventory largely occur where there is<br />

<strong>in</strong>sufficient source activity <strong>in</strong>formation available to make an estimate of<br />

emissions. In recent years, the NAEI has closed many of the gaps <strong>in</strong> the<br />

<strong>in</strong>ventory for anthropogenic and some natural sources, but acknowledges the<br />

very high levels of uncerta<strong>in</strong>ties associated with some of their estimates, e.g.<br />

for bonfires, small-scale burn<strong>in</strong>g of waste, natural fires, etc. However, a number<br />

of gaps still rema<strong>in</strong> <strong>in</strong> specific areas or for some additional processes <strong>in</strong> sectors<br />

which are already covered <strong>in</strong> the <strong>in</strong>ventory. These <strong>in</strong>clude emissions from:<br />

• certa<strong>in</strong> arable farm<strong>in</strong>g processes and harvest<strong>in</strong>g;<br />

• domestic cook<strong>in</strong>g and barbecues;<br />

• build<strong>in</strong>g demolition processes;<br />

• certa<strong>in</strong> quarry<strong>in</strong>g processes such as blast<strong>in</strong>g and fill<strong>in</strong>g of used quarries;<br />

• certa<strong>in</strong> fugitive emissions <strong>in</strong> the metals <strong>in</strong>dustry (e.g. smelt<strong>in</strong>g); and<br />

• use of munitions by military operations and for quarry<strong>in</strong>g.<br />

39. Without construct<strong>in</strong>g an <strong>in</strong>ventory, it is impossible to judge the magnitude<br />

of these emissions, but the sources are ranked above <strong>in</strong> an anticipated<br />

decreas<strong>in</strong>g order of importance to emissions on a national scale. However, <strong>in</strong><br />

some locations and at certa<strong>in</strong> times, these sources could make a significant<br />

contribution to local emissions, e.g. from build<strong>in</strong>g demolition.<br />

4.3 Quantify<strong>in</strong>g the emissions of <strong>PM2.5</strong> precursor gases,<br />

their conversion to particles and their spatial<br />

distribution<br />

40. Emissions of <strong>PM2.5</strong> precursor gases from anthropogenic sources <strong>in</strong> Europe<br />

are also estimated by <strong>in</strong>ventories and reported by countries to CLRTAP. The<br />

NAEI provides a time series for UK emissions of the precursors NOx, SO2, nonmethane<br />

volatile organic compounds (NMVOCs) and NH3 from 1980-2009 and<br />

projections to 2020. These four pollutants are those covered under the National<br />

Emission Ceil<strong>in</strong>gs (NEC) Directive which sets national emission ceil<strong>in</strong>gs for each<br />

of these pollutants for EU member states to be met by 2010. Emissions are<br />

estimated <strong>in</strong> the same way as for <strong>PM2.5</strong> us<strong>in</strong>g sector-specific emission factors<br />

and activity data.

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